Zinc oxide nanoparticles alleviate the arsenic toxicity and decrease the accumulation of arsenic in rice (Oryza sativa L.)
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Yan et al. BMC Plant Biology (2021) 21:150
https://doi.org/10.1186/s12870-021-02929-3
RESEARCH ARTICLE Open Access
Zinc oxide nanoparticles alleviate the arsenic
toxicity and decrease the accumulation of
arsenic in rice (Oryza sativa L.)
Shiwei Yan1†, Fan Wu1†, Song Zhou1, Jianhao Yang1, Xianjin Tang2* and Wenling Ye1,2*
Abstract
Background: Rice is particularly effective, compared to other cereals, at accumulating arsenic (As), a nonthreshold,
class 1 human carcinogen in shoot and grain. Nano-zinc oxide is gradually used in agricultural production due to
its adsorption capacity and as a nutrient element. An experiment was performed to explore the effects of zinc
oxide nanoparticles (nZnO) on arsenic (As) toxicity and bioaccumulation in rice. Rice seedlings were treated with
different levels of nZnO (0, 10, 20, 50, 100 mg/L) and As (0, and 2 mg/L) for 7 days.
Results: The research showed that 2 mg/L of As treatment represented a stress condition, which was evidenced by
phenotypic images, seedling dry weight, chlorophyll, and antioxidant enzyme activity of rice shoot. The addition of
nZnO (10–100 mg/L) enhanced the growth and photosynthesis of rice seedlings. As concentrations in the shoots
and roots were decreased by a maximum of 40.7 and 31.6% compared to the control, respectively. Arsenite [As (III)]
was the main species in both roots (98.5–99.5%) and shoots (95.0–99.6%) when exposed to different treatments.
Phytochelatins (PCs) content up-regulated in the roots induced more As (III)-PC to be complexed and reduced As
(III) mobility for transport to shoots by nZnO addition.
Conclusion: The results confirmed that nZnO could improve rice growth and decrease As accumulation in shoots,
and it performs best at a concentration of 100 mg/L.
Keywords: Arsenic, Zinc oxide nanoparticle, Toxicity, Speciation, Rice
* Correspondence: xianjin@zju.edu.cn; wlye@ahau.edu.cn
†
Shiwei Yan and Fan Wu are co-first author.
2
Key Laboratory of Environment Remediation and Ecological Health
(Zhejiang University), Ministry of Education, Hangzhou 310058, China
1
Anhui Province Key Laboratory of Farmland Ecological Conservation and
Pollution Prevention, School of Resources and Environment, Anhui
Agricultural University, 130 Changjiang West Road, Hefei 230036, Anhui, P.R.
China
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data made available in this article, unless otherwise stated in a credit line to the data.Yan et al. BMC Plant Biology (2021) 21:150 Page 2 of 11 Background studied to evaluate the effects of nZnO (10–100 mg/L) Arsenic (As) is a carcinogenic metal that enters the body on As stress, including dry weight, chlorophyll content, primarily through drinking water and diet, which in- root cell membrane integrity, leaf antioxidant enzyme creases human health risks and attracts global attention activity and As accumulation in rice. It’s assumed that [1]. Human activities increase the concentration of ar- nZnO can reduce the toxicity of As in rice by promoting senic in soil and water, thereby increasing the concentra- the growth and reducing the concentration of As in rice tion of arsenic in crops [2]. Paddy rice (Oryza sativa L.) seedlings. In this study, the effects of different doses of is particularly efficient in As uptake from paddy soil due nano-zinc oxide on physiological status and arsenic ac- to rice plants’ unique ability [3, 4]. Elevated As accumu- cumulation in rice were investigated to better under- lation in rice has the potential to become a new disaster standing the mechanism and optimal dosing of nano- for the population in Southeast Asia [5], it is important zinc fertilizer to reduce arsenic concentration in plants. to reduce the accumulation of arsenic in rice. This study will provide a new insight to nanomaterials’ It has been reported that arsenic poisoning of plants possible application in environmental remediation. will lead to shorter rhizomes, reduced biomass and inhibited photosynthesis [6]. Khan et al. found that both the biomass and length of Indian mustard root and stem Materials and methods were reduced under arsenic treatment [7]. Szilvia et al. Chemicals found that excessive uptake of arsenic reduced chloro- nZnO was purchased from Nanjing XFNANO Material phyll content of maize and sunflower leaves [8]. In Technology Co., Ltd. with a purity of 99%. Scanning addition, plants under As stress produce a large amount electron microscopy (SEM) was used to observe that of reactive oxygen species (ROS) [9]. As also exacerbates nZnO were mostly spherical, with a particle size of 20- the extent of cell membrane damage caused by mem- 30 nm and a specific surface area of 21.50 m2/g. Sodium brane lipid peroxidation [10]. arsenite (NaAsO2) was purchased from Aladdin Chem- Nanoparticles (NPs) show great potential in the re- ical Co., Ltd. mediation of soil and water pollution for their high sur- face area, gap structure and unique property [11]. It’s reported that kinds of NPs can reduce the damage of Experiment design toxic metals to plants. For instance, CuO NPs enhanced Rice seeds (Liangyou 8106) were purchased from the growth and decreased As accumulation in rice [12]. Win-all Hi-tech Seed Co., Ltd. The collection of plant In addition, 500 mg/kg multiwall carbon nanotubes have material comply with national guidelines and legisla- been reported to alleviate Cd-induced toxicity by pro- tion. The seeds were surface-sterilized with 0.5% moting plant growth [13].. Singh et al. found that TiO2 NaOCl solution for 15 min, washed with deionized NPs application reduced Cd toxicity of the soybean water and then soaked for 1 h with deionized water plants by increasing the photosynthetic rate and growth [23]. After seed germination, rice seedlings were parameters [14]. In recent years, nZnO have been widely transferred to pots containing 1 L Kimura nutrient so- used as crop nutrients in zinc-deficient areas. nZnO had lution [24]. There were two rice seedlings per pot. the positive effects on plant growth and physiology [15, The pots were placed randomly in a growth cabinet 16]. What’s more, the positive impacts of nZnO on alle- at 25 °C, 16 h photoperiod with a light intensity of viation of Cd accumulation in several plant species have 350 μmol/m2s. The nutrient solution in the pots was been reported [17–20]. To date, the impact of nZnO on renewed every 3 days. the plant growth and As uptake of rice exposed to As Rice seedlings cultivated with Kimura nutrient solution stress is rarely studied. Wang et al. recently researched for 30 days were used as experimental materials. Pour the effects of nZnO on As uptake, but the As concentra- out the nutrient solution and dilute the prepared As and tion treated was 1 mg/L, at which concentration rice nZnO stock solutions into the pot to obtain the target growth wasn’t affected significantly [21]. In addition, gradient treatment. NaAsO2 was added to prepare As- only one nZnO dose (100 mg/L) application was spiked solution with As concentration of 2 mg/L, nZnO researched in the experiments. Therefore, a Zn dose- was applied to prepare test solution of 0, 10, 20, 50, 100 response curve is needed to find the optimal concentra- mg/L Zn (nZnO). The nZnO suspension was sonicated tion of nZnO which can reduce the As toxicity. by ultrasonic vibration (100w, 40KHz) for 45 min to in- Seed germination and the early seedling growth are crease dispersion. The treatments were as follows (As more sensitive to metal pollution, and the early seedling concentration (mg/L)) + nZnO concentration (mg/L)): growth are important considerations in toxicity assess- As; As+nZnO10; As+nZnO20; As+nZnO50; As+ ment [22]. In this experiment, the growth and physio- nZnO100. Treatments with no As and nZnO were con- logical characteristics of rice seedlings (30 d) were trols. Each treatment was repeated 3 times.
Yan et al. BMC Plant Biology (2021) 21:150 Page 3 of 11
Biomass Electrolyte leakage
Rice seedlings were harvested after exposure to treatments Electrolyte leakage was measured using root samples to com-
for 7 days. The roots were soaked with a 10 mM ethylenedi- pare the change of cell membrane permeability. The proced-
aminetetraacetic acid solution for 10 min and then washed ure of determination was based on the method used before
with distilled water 3 times. After washing the above-ground [27]. After the roots were rinsed, a certain amount (0.5 g) of
part of each rice with distilled water, the two rice seedlings fresh root sample was weighed and placed in a 50 ml test
in each pot were treated separately. One was kept fresh to tube, and 30 ml of distilled water was added and shaken in a
measure chlorophyll content, antioxidant enzyme activities, constant temperature shaker (25 °C) for 1 h to determine the
and electrolyte leakage. The other one was oven-dried at initial conductivity EC0. Then the root samples were boiled
75 °C for 72 h to constant weight. for 10 min to destroy the membrane permeability. The final
electrical conductivity (ECt) was measured after equilibration
Chlorophyll content at 25 °C. Electrolyte leakage (%)=(EC0/ECt)×100%.
The harvested fresh rice leaf sample was cut into pieces,
0.1 g sample was weighed into a centrifuge tube, and 10 Detection of As and Zn concentration in different tissues
ml of 95% (v / v) ethanol was added. After being left in of rice
the dark for 14 h, the absorbance of the supernatant was The total As and Zn in plant tissues were determined by
measured with a UV-422G spectrophotometer at wave- strong acid digestion. Approximately 0.5 g of dry root and
lengths of 649 nm and 665 nm. Use the formula (1) and dry shoot were added into a 5 mL high-purity HNO3/HClO4
(2) to calculate chlorophyll a (Chl a) and chlorophyll b (87/13, v/v) and sat overnight at room temperature for predi-
(Chl b), separately [25]. Total chlorophyll is the sum of gestion. Total As and Zn concentrations in the samples were
chlorophyll a and chlorophyll b. analyzed using ICP-MS (Agilent 7500ce). We used the
GBW10023 (GSB-14) for standard reference material. The
chlorophyll a ¼ ð13:95A665 − 6:8A649 Þ ðmg=LÞ recovery for reference material was 86.5–97.3%.
10
10 − 3 ðLÞ=fresh weight ðgÞ ð1Þ As speciation analysis
For determination of As speciation in rice tissues, fresh rice
chlorophyll b ¼ ð24:96A649 − 7:32A665 Þ ð2Þ
samples were grounded by liquid nitrogen. 0.25 g materials
total chlorophyll ¼ chlorophyll a were extracted using a 20 mL PBS solution for 1 h with sonic-
þ chlorophyll b ð3Þ ation. The PBS solution contained 2 mM NaH2PO4 and 0.2
mM Na2-EDTA (pH 6.0). The extracts were filtered through
0.45 μm filters as described previously [28]. For quality assur-
Determination of antioxidant enzyme activities ance, we added a certified reference material (NIST 1568a rice
Fresh shoot and root samples were used for testing the flour) and included blanks. The recovery for reference material
antioxidant enzyme activities and Phytochelatins (PCs) was 88.4–109.1%. High Performance Liquid Chromatography–
content, respectively. Fresh samples (0.5 g) were weighed Inductively Coupled Plasma Mass Spectrometry (HPLC-ICP-
and grounded in liquid nitrogen, then added 5 ml 0.01 MS; 7500a Agilent Technologies) was used for As speciation.
mol/L PBS buffer solution (pH 7.0). The 0.01 mol/L PBS
buffer solution was prepared by mixing dissolving 7.9 g Translocation factor of As in Rice
NaCl, 0.2 g KCl, 0.24 g KH2PO4, and 1.8 g K2HPO4 in 1 Translocation factor (TF) of As was defined as the ratio of As
L deionized water. The homogenate was centrifuged at concentration in shoots to that in roots [23], as described below:
20,000×g for 20 min. Then the supernatant was collected
to determine the activity of catalase (CAT), superoxide As concentra tion in shoots ðmg=kgÞ
TF ¼
dismutase (SOD), and PCs as described before [26]. The As concentra tion in roots ðmg=kgÞ
specific method is as follows, 10 μL supernatant was
added to testing wells which already contain 40 μL sam-
ple dilution. The wells were incubated for 30 min at Statistical analysis
37 °C after closing plate with closure plate membrane. Statistical analysis was performed using Microsoft Excel
Then, 50 μL HRP-conjugate reagent was added to each 2010 and SPSS-19.0 software. The statistical difference
well, except blank well. Chromogen solution A and among control and treatments was determined using
chromogen solution B were added to each well for 15 one-way ANOVA multiple comparison. Data were com-
min at 37 °C. Subsequently, the stop solution was added pared by Duncan’s test. Differences were considered sig-
to each well to stop the reaction. Finally, we take the nificant at p ≤ 0.05. Pearson correlation analysis was
blank well as zero and read absorbance at 450 nm after performed by SPSS to quantify the relationships between
adding the stop solution within 15 min. Zn concentration and As concentration in rice.Yan et al. BMC Plant Biology (2021) 21:150 Page 4 of 11 Fig. 1 Biomass of the shoots and roots of rice seedling grown in different treatments Fig. 2 Phenotypic images of rice seedlings after 7 days of growth in different treatments
Yan et al. BMC Plant Biology (2021) 21:150 Page 5 of 11
Results
Growth analysis
To investigate the impacts of nZnO on rice seedlings
growth under As stress, rice growth parameters were re-
corded and depicted in Figs. 1 and 2. It’s showed that 2
mg/L As treatment greatly reduced the dry biomass of
shoots. The addition of nZnO (10–100 mg/L) improved
the rice resistance to As toxicity, increasing the biomass of
shoots and roots by 19.2–59.6% and 6.7–26.7%, respect-
ively. The shoot dry weight was almost closed to the con-
trol when applied with 50 mg/L nZnO.
Chlorophyll content
Chlorophyll is an important substance for plants to ab-
sorb sunlight for photosynthesis, and its content affects Fig. 4 Structural damage to the plasma membrane
the growth rate of plants. As shown in Fig. 3, the chloro-
phyll content of rice leaves treated with 2 mg/L arsenic
Antioxidant enzyme activities of rice shoot
was significantly decreased (27.3%) compared to the
To determine how the presence of nZnO affects the tox-
control (p < 0.05). After application with nZnO, the
icity of As on plants, the changes of SOD and CAT ac-
chlorophyll concentration increased by 2.7–20.3%. Simi-
tivity in rice shoots exposed to different treatments for
larly to the shoot biomass, the chlorophyll content was
7 days were studied. Results showed that the SOD activ-
most in the As+nZnO50 treatment and had no signifi-
ity in shoots decreased by 34.46% in 2 mg/L As treat-
cant difference with control (p > 0.05).
ment compared to that of control (Fig. 5a). SOD activity
was increased by 35.34, 17.13, 16.71 and 26.37%, respect-
Change of the cell membrane permeability ively, for As+nZnO10, As+nZnO20, As+nZnO50 and
Electrolyte leakage was used to analyze membrane per- As+nZnO100 treatments than As treatment. Especially
meability. Figure 4 shows that As treatment induced ob- in the 20 mg/L nZnO treatment, SOD activity has
vious electrolyte leakage, increasing the electrolyte returned to normal levels. The change in CAT activity is
leakage by 1.75 times compared with control, from 8.8 shown in Fig. 5b. There was no significant difference in
to 15.4%. The addition of nZnO significantly increases CAT activity between the different treatments (p > 0.05).
the electrolyte leakage. And with the increase of concen-
tration of nZnO treatment, the electrolyte permeability Uptake of As and Zn in rice tissues
also gradually increases. Especially for the As+nZnO100 The concentrations of As and Zn in plant tissues are
treatment, the electrolyte leakage increased to 31.8%, in- shown in Figs. 6 and 7. Application of nZnO decreased
dicating that the addition of nZnO will synergize with the As contents in rice shoots by 14.3–40.7% (Fig. 6a).
As to change the permeability of the cell membrane. But in the roots, the effects of nZnO application on As
accumulation were different, which depended on the
nZnO dose application (Fig. 6b). 10 mg/L and 20 mg/L
nZnO addition didn’t decrease the As concentration,
while 50 mg/L and 100 mg/L treatments decreased the
As concentration by 25.6 and 31.6%, respectively, in rice
roots. TF of As in different treatments were calculated
(Table 1). The results showed different concentration
applications of nZnO significantly decreased the TF
values. In all treatments, As (III) was the main species in
both roots (98.6–99.3%) and shoots (95.01–99.58%), as
showed in Table 2. nZnO caused little impact on the As
(III) species percentage in rice roots (p > 0.05) but sig-
nificantly reduced As (III) percentage in rice shoots (p <
0.05). Moreover, Zn concentration in shoots and roots
was also determined (Fig. 7). Zn content in rice roots
and shoots were promoted with the application of nZnO
Fig. 3 Effect of nZnO on Chlorophyll content under As stress
increased. After calculating, we found that AsYan et al. BMC Plant Biology (2021) 21:150 Page 6 of 11
Fig. 5 Effects of different treatments on SOD (a) and CAT (b) activities in rice leaves
concentration had a negative correlation with Zn con- Discussion
centration in rice shoots, and the Pearson correlation co- In this study, we researched the effects of different con-
efficient was − 0.973. centrations of nZnO on the rice growth and As accumu-
lation under hydroponic conditions, to test whether
nZnO can be used as an environmental-friendly agri-
PCs content of rice root chemical to reduce As toxicity in rice. This experiment
For further understanding As transport in rice plants, shows that the application of nZnO can promote the
PCs content in rice roots were researched (Fig. 8). PCs rice biomass under As stress, especially for the treatment
content in rice root was 115.5 ng/L when treated with 2 of As+nZnO50 (Fig. 1). Our early germination experi-
mg/L As. nZnO application (10–100 mg/L) significantly ments also showed that low concentration of nZnO (10,
promoted PCs content by 8.2–24.1%. 20 mg/L) amendment increased the shoot length byYan et al. BMC Plant Biology (2021) 21:150 Page 7 of 11 Fig. 6 As concentration in rice shoots (a) and roots (b) 13.1–14.1% and shoot weight by 15.1–41.2%, respectively than 100 mg kg− 1, the As concentration in the shoots [29]. It’s reported that kinds of NPs increase the growth and roots will be further reduced, because more As will of plants under metal stress. For example, Liu et al. be adsorbed before entering the rice root, similar to our found that nCuO treatment promoted rice growth and previous stuy [29]. But it also needs to be noted that reduced absorption of As [12]. Similarly, it’s depicted high concentration of nZnO can cause poison to plants that nZnO application improved the height, number of and reduce the biomass of rice. leaves, shoot and roots dry biomass of maize plants Chlorophyll is an important substance for plants to ab- grown on a Cd-contaminated soil [19]. Studies have sorb sunlight for photosynthesis. The amount of chloro- shown that Zinc NPs and Zn positively influenced the phyll affects the growth rate of plants, so it can be used growth of sorghum and nutritional status of the plants as an important indicator to measure the degree of stress [30, 31]. Besides, the promoted biomass with nZnO ap- of heavy metals on plants [32]. Research by Rahman plication might be associated with the decreased metal et al. showed that the chlorophyll content in rice is posi- stress in rice. At the same time, it can be inferred from tively correlated with shoots growth [33], which is con- Fig. 6 that when the amount of nZnO applied is greater sistent with our results. Arsenic interfere with the
Yan et al. BMC Plant Biology (2021) 21:150 Page 8 of 11 Fig. 7 Zn concentration in rice shoots (a) and roots (b) activity of chlorophyll synthase and hinder the synthesis a great role in photosynthesis induced the increase of of chlorophyll [34]. When the photosynthesis of the chlorophyll concentration. Recent studies found that the leaves is weakened, the carbohydrates produced are re- application of nZnO increased the chlorophyll content duced so that the biomass of the shoots is decreased. of plants under Cd and Pb stress [17, 20]. The present study also indicated that with the applica- Oxidative stress is generally considered to be possible tion of nZnO (10–100 mg/L), the chlorophyll concentra- mechanisms of phytotoxicity caused by heavy metals. tion gradually increased, and the shoots biomass showed The photosynthesis of chloroplasts is disturbed under the same trend (Figs. 1 and 3). It’s assumed that Zn plays arsenic, which causes oxygen to become its electron Table 1 TF of the rice exposed to different treatments (mean ± SE, n = 3) Treatment As As+nZnO10 As+nZnO20 As+nZnO50 As+nZnO100 TF 0.020 ± 0.0011a 0.0155 ± 0.0001b 0.0135 ± 0.002b 0.0176 ± 0.0037ab 0.0170 ± 0.0017b
Yan et al. BMC Plant Biology (2021) 21:150 Page 9 of 11
Table 2 Summary of total arsenic and ratio of As (III) in rice tissues grown in different treatments (mean ± SE, n = 3)
Treatment Rice compartment Total As (mg/kg dry weight) The ratio of As (III)(%)
As Shoot 19.67 99.58 ± 1.15 A
As+nZnO10 Shoot 16.85 95.50 ± 2.03 B
As+nZnO20 Shoot 14.44 95.90 ± 2.35 B
As+nZnO50 Shoot 13.17 95.32 ± 3.01 B
As+nZnO100 Shoot 11.66 95.01 ± 2.85 B
As Root 989.38 99.01 ± 6.03 a
As+nZnO10 Root 1084.75 98.06 ± 7.84 a
As+nZnO20 Root 1077.04 99.30 ± 10.10 a
As+nZnO50 Root 736.08 98.68 ± 5.32 a
As+nZnO100 Root 677.22 99.32 ± 8.32 a
acceptor, and the metabolite ROS is also produced [35]. nZnO (20–100 mg/L) was added in our experiment. The
Subsequently, in order to prevent oxidative stress, plants following electrolyte leakage data also show that the
can actively activate various enzyme and non-enzyme addition nZnO of aggravated membrane lipid peroxida-
defense systems [36]. The SOD is the first defense en- tion. Differently, in our early germination experiments,
zyme that catalyzes the more toxic O2− to less toxic CAT activity had the same trend with SOD activity, but
H2O2 [37]. However, our results showed that 2 mg/L As it was not significantly affected in the current
treatment decreased SOD activity compared with the experiment.
control significantly (Fig. 5a). The reason might be that The concentration of As in rice shoots decreased with
the high concentration of arsenic destroys the antioxi- the increase of nZnO concentration (Fig. 6a), while the
dant reaction mechanism of rice. SOD activity increased As concentration in rice roots depended on the nZnO
with the addition of nano-zinc oxide, indicating that concentration. Low concentration nZnO (10–20 mg/L)
nZnO promoted the response of rice antioxidant mech- treatments increased the content of As in roots, but high
anism. Due to the strong adsorption capacity of nano concentration nZnO (50–100 mg/L) treatments signifi-
zinc oxide, arsenic is adsorbed before it enters the rice cantly reduced the concentration of As in the roots (Fig.
plant, thus protecting the antioxidant mechanism of rice 6b). To investigate the cause of this phenomenon in the
[38]. Wang et al. found that SOD activity was up- roots, we studied the permeability of the root cell plasma
regulated by nZnO in tomato plants, supported by en- membrane. The plasma membrane is selectively perme-
hancing transcription of Cu/Zn2-SOD and Fe-SOD genes able, which controls the transport and exchange of sub-
[39]. On the other hand, previous studies have reported stances inside and outside the cell. Electrolyte leakage
that nZnO can promote the generation of ROS in rice was further used to detect the membrane permeability.
plants [40]. This is consistent with the results that SOD The results of this study found that As treatment signifi-
activity decreased again when high concentration of cantly disrupted the integrity of the root cell membrane
and the application of nZnO aggravate the destruction
of the root cell membrane (Fig. 4). This may be caused
by high Zn concentration in the nutrient solution re-
leased by nZnO (Figure S2). As mentioned above, stud-
ies have found that excessive Zn can cause peroxidation
of plant root membrane esters, leading to further dam-
age to cell membranes [41]. Therefore, the application of
low concentration nZnO (10–20 mg/L) cannot reduce
the absorption of As by roots. Although 50–100 mg/L
nZnO application also aggravates the destruction of the
root cell membrane, As concentration in the roots were
significantly decreased because the As concentration in
the nutrient solution was significantly decreased by the
strong adsorption of nZnO (50–100 mg/L) (Figure S1).
Unlike the roots, As concentration in the shoots contin-
ued to decline with the nZnO increasing application.
Fig. 8 Effects of different treatments on PCs content in rice roots
What happened when As transported from root toYan et al. BMC Plant Biology (2021) 21:150 Page 10 of 11
shoot? Transport factor (TF) was calculated, which is concentration in nutrient solution of different treatments when rice was
used to calculate the transport capacity of As in plants harvested.
[26, 42]. It’s found that the nZnO application (10–100
mg/L) decreased As TF when rice was exposed to As Acknowledgements
stress. As speciation in rice tissues and PCs concentra- We thank the school of Resources and Environment, Anhui Agricultural
University, Hefei, China for the assistance.
tion in roots explained the phenomenon. We found that
As speciation in rice roots and shoots was dominated by Authors’ contributions
arsenite (95.01–99.58%) as reported by other reports [43, Wenling Ye and Xianjin Tang conceived and designed the study. Shiwei Yan,
44]. There is no significant difference of the As speci- Fan Wu, Song Zhou, and Jianhao Yang performed the experiments. Wenling
Ye wrote the paper. Xianjin Tang reviewed and edited the manuscript. All
ation in the roots when rice plants treated with nZnO, authors read and approved the manuscript.
but arsenite percentages in the shoots were significantly
decreased by nZnO application. Besides, we found that Funding
PCs concentration in rice roots were significantly up- We acknowledge Provincial Natural Science Foundation of Anhui
(2008085MD112), the Fundamental Research Funds for the Central
regulated by the nZnO application. So it’s assumed that Universities (2019FZJD007), Anhui Science and Technology Major Project
nZnO application up-regulates the PCs concentration in (No.18030701186) and the Open Fund of Anhui Province Key Laboratory of
rice roots, causing more As (III) stored in the root cell Farmland Ecological Conservation and Pollution Prevention (FECPP201904).
vacuole in combination with PCs [45]. Then the As (III) Availability of data and materials
transport to the shoot was suppressed, causing the ar- The datasets used and/or analyzed during the current study are available
senic concentration and the arsenite percentage also de- from the corresponding author on reasonable request.
creased in the shoots. Another possible reason is that
Declarations
the increase of Zn promoted the growth of plant shoots
(Fig. 1), then the concentration of As in the shoots was Ethics approval and consent to participate
diluted by the increasing biomass. The negative correl- Not Applicable.
ation between As concentration and Zn concentration
Consent for publication
also indicated that the addition of nZnO played a posi- Not Applicable.
tive role in the reduction of arsenic in rice shoots.
On the other hand, the application of nZnO increases the Competing interests
On behalf of all authors, the corresponding author (Wenling Ye) states that
concentration of Zn in rice shoots and roots (Fig. 6). Zinc there is no conflict of interest.
concentration in shoots and roots of rice showed the increas-
ing trend with nZnO applied. nZnO have been used as a Received: 23 December 2020 Accepted: 18 February 2021
source of fertilizer in many studies to improve plant growth
[15, 46]. It has been shown that application of 200 mg/L References
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